Pelecaniformes
Double-crested Cormorant (Phalacrocorax auritus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.633 | Survival, modeled average (Adult, at least 4 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Striped mullet: 25.5, gulf menhaden: 17.6, hardhead catfish: 11.8, Sciaendiae: 15.7, unidentifiable fish: 5.9 | Frequency | % | Not Reported | 51 | Lavaca bay | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | See citation | Breeding pairs/location | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Pre-goby: 13.2, Transition 12.8, Post-goby: 17.0 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 1187, Transition 518, Post-goby: 1404 | Strachan Island | Exposure Factor Datasets | CANADA |
Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | See citation | Three sites along St. Lawrence River | Exposure Factor Datasets | CANADA |
Dietary Composition | Pre-goby: 14.4, Transition 14.3, Post-goby: 20.1 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 3100, Transition 2206, Post-goby: 1028 | Griswold Island | Exposure Factor Datasets | CANADA |
Dietary Composition | Pre-goby: 11.9, Transition 12.7, Post-goby: 16.7 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 923, Transition 1631, Post-goby: 2035 | McNair Island | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | 2006: >93% alewife, 2007: 86.5%; balance made up of round goby, rainbow smelt, pumpkinseed | Chick diet | % by mass | B | Adult | Tommy Thompson Park, Lake Ontario | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 2008: 1.79 ± 0.03, 2009: 1.96 ± 0.02 | Brood size | Number of hatchlings | NR | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA |
Time of Hatching or Parturition | 2008: June 4, 2009: May 29 | Earliest hatch date | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA | ||
Hatching Success | 2008: 49.5% [45.9-52.9 (95% CI)], 2009: 59.4% [55.8-63.1 (95% CI)] | Fledge success | Hatchling | 2008: 28, 2009: 25 | Northeast SD | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Pre-goby: 10.15, Transition 10.25, Post-goby: 14.81 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 17490 sq km | sq km | B | Adult | 37 | Mississipi Alluvial Valley (AR, MS, LA) & Upper Coastal Plain (AL, MS) | Exposure Factor Datasets | Over-wintering populations | USA | 1986 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Figure 2 | Active nests/11,000 ha | Adult | Estero Bay Aquatic Preserve | Exposure Factor Datasets | Breeding | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | 1990: 3985, 1994: 9854, 1997: 8217, 2000: 12821, 2003: 11470 | Number of nests | Number of nests | Georgian Bay, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
Population Density | 1990: 4310, 1994: 7281, 1997: 8494, 2000: 12441, 2003: 11527 | Number of nests | Number of nests | North Channel, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Herring, shad: 0.6, Peamouth/Pikeminnow: 24.0, Sucker: 5.8, Smelt: 0.3, Salmonid: 45.5, Stickleback: 5.0, Sculpin: 8.0, Surfperch: 0.3, Flounder: 8.5, Other: 1.8 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 206 | Rice Island/Channel Markers | Exposure Factor Datasets | USA |
Dietary Composition | Herring, shad: 27.8, Peamouth/Pikeminnow: 0.7, Sucker: 4.7, Smelt: 7.6, Salmonid: 15.9, Stickleback: 2.1, Sculpin: 9.2, Surfperch: 7.3, Flounder: Pacific sand lance: 1.8, Flounder: 9.8 Other: 1.3 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 128 | East Sand Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number before alewife eastablishment | % | Exposure Factor Datasets | USA | |
Dietary Composition | Alewife ,cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number after alewife eastablishment | % | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets | USA |
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent composition and biomass | B | Adult | Exposure Factor Datasets | Leech Lake | USA | |
Dietary Composition | See citation | Percent composition and biomass | B | Chick | Exposure Factor Datasets | Leech Lake | USA |
Brown Pelican (Pelecanus occidentalis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | 0.83 | Percentage of diet that is anchovy+sardine | NR | Midriff Islands | Exposure Factor Datasets | MEXICO |
Dietary Composition | See citation Figure 3 | Proportion of anchovy:sardine | NR | Midriff Islands | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Hatching Success | 0 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.677 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.635 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.576 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.695 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.588 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.646 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.5 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.537 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|
Population Density | See citation Table 2 | Nests/ha/year | Adult | Coastal LA | Exposure Factor Datasets | USA |
Population Density | See citation Table 2 | Colonies/ha/year | Both Adults and Juveniles | Coastal LA | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|
Population Density | See citation Table 2 | Breeding pairs/ha | Adult | North central Chilean islands | Exposure Factor Datasets | CHILE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|
Population Density | Review | Number of nests in colonies that nest in mangroves | Small Islands of Bahía Santa María- La Reforma, Sinaloa, México |
Exposure Factor Datasets | CHILE | ||
Population Density | 2011: 88-289 2012: 120-1895 | Number of nests/583 sq km | 2-3 surveys/y | Small Islands of Bahía Santa María- La Reforma, Sinaloa, México |
Exposure Factor Datasets | CHILE | 2011 & 2012: 12-159 SE |
Time of Mating/ Laying | January | 2-3 surveys/y | Small Islands of Bahía Santa María- La Reforma, Sinaloa, México |
Exposure Factor Datasets | CHILE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Population Density | 1722 | Number of individuals (area size NR) | Both Adults and Juveniles | 1722 | Three sites in Jacksonville, FL | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | Review | Number of individuals/sq km | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation | Number of breeding pairs (area size NR) | Adult | West coast US/Mexico border | Exposure Factor Datasets | Breeding | MEXICO |
Population Density | See citation | Number of individuals (area size NR) | Both Adults and Juveniles | West coast US/Mexico border | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|
Population Density | See citation; fewer nests in ENSO years | Number of nests on islands of Gulf of Mexico 1970-2006 during ENSO/non-ENSO years | Gulf of Mexico | Exposure Factor Datasets | Breeding | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | 466 nests | Number of nests/>50,314 ha | Gulf of Chiriquí | Exposure Factor Datasets | PANAMA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Population Density | 0-910 | Number of individuals/90 sq km (temporal) | San Nicolas Island | Exposure Factor Datasets | Ventura | USA |
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
PCB | 0.08 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
<5 ppm: 95%, >5 ppm: 86% | Young survived 7-10 days | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | |||
MERCURY COMPOUNDS | LCRS: 0.54, reference site: 0.17 µg/g ww | Egg concentration | Embryo | LCRS: 26, reference: 42 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 14.2, 2003: 14.4, 2004: 15.2 g | Liver weight | Not Reported | Nestling | 2002: 2, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 0.23, 2003: 0.23, 2004: 0.19 µg/g ww | Brain concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
DIELDRIN | MS-90: 0.0258, BI-82: 0.0926, BI-89: 0.0270, BI-90: 0.0661, WM-89: 0.0308 WM-90: 0.0204, WM-91: 0.00887, SW-91: 0.0275 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
MERCURY (elemental) | 0.81 ± 0.50 µg/g dw | Feather concentration | Both Male and Female | Nestling | 10 | Georgia & South Carolina | Toxicity Factor Datasets | USA |
DDE (2,4'-) | 4.2 ppm ww | Egg concentration | Embryo | 10 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
<5 ppm: 0.232, >5 ppm: 0.201 mm | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | ||||
MERCURY COMPOUNDS | LCRS: 0.65 µg/g ww | Egg concentration | Embryo | 20 | Carson Lake & Lahontan Reservoir | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 12.8, 2003: 15.2, 2004: 13.0 g | Liver weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 20.45, 2003: 36.38 µg/g ww | Feather concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
DDD (4,4'-) | MS-90:0.0222, BI-82: 0.246, BI-89: 0.0180, BI-90: 0.0473, WM-89: 0.0168, WM-90: 0.0098, SW-91: 0.0683 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
METHYLMERCURY | Review, see citation Figure 2 | Egg concentration | Embryo | Not reported | Toxicity Factor Datasets | USA | ||
DDD (2,4'-) | 0.12 ppm ww | Egg concentration | Embryo | 4 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 0.15 µg/g [0.05-0.31 (95% CI)] | Embryonic LD50 | Embryo | 63 | Patuxent Wildlife Research Center | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 423, reference: 422 g | Body weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | Lahontan Reservoir: 3.55, Humboldt River: 3.59 g | Kidney weight | Not Reported | Nestling | 7 | Lahontan Reservoir: contaminated site; Humbodlt River: reference site | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 6.66, 2003: 8.50 µg/g ww | Feather concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
DDT (4,4'-) | MS-90: 0.0122, BI-89: 0.0282, BI-90: 0.0506, WM-89: 0.0185, WM-90: 0.0236, SW-91: 0.0572 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
METHYLMERCURY | Review, see ciation Figure 3 | Feather concentration | Not Reported | Not reported | Toxicity Factor Datasets | USA | ||
DDT (2,4'-) | 0.46 ppm ww | Egg concentration | Embryo | 6 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 1997: 0.60, 1998: 1.20 µg/g ww | Stomach concentration | Both Adults and Juveniles | 1997: 4, 1998: 6 | Lahontan Reservoir | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 13.73, reference: 12.44 g | Liver weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 0.170, 2003: 0.646, 2004: 0.262 g | Spleen weight | Not Reported | Nestling | 2002: 2, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
PCB | 2.49 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA |
BORON COMPOUNDS | BI-89: 0.408, WM-89: 0.395, WM-91: 0.859, SW-91: 1.29 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDE (2,4'-) | 4.8 ppm ww | Egg concentration | Embryo | 9 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
DIELDRIN | 0.02 ppm ww | Egg concentration | Embryo | 2 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 1997: 0.53, 1998: 1.12 µg/g ww | Stomach concentration | Both Adults and Juveniles | 1997: 4, 1998: 6 | Lahontan Reservoir | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 4.78, reference: 4.56 g | Kidney weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 0.170, 2003: 0.646, 2004: 0.626 g | Spleen weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
PCB | 1982: 3.32, 1989: 1.23, 1990: 5.38 µg/g ww | Egg concentration | Not Reported | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA |
BARIUM (elemental) | BI-89: 0.259, WM-89: 0.351, SW-91: 0.823 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDD (2,4'-) | 0.16 ppm ww | Egg concentration | Embryo | 6 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 1997: 0.31, 1998: 0.61 µg/g ww | Stomach concentration | Both Adults and Juveniles | 5 | Carson Lake | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 0.28, reference: 0.50 g | Spleen weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 2.41, 2003: 2.04, 2004: 1.66 g | Brain weight | Not Reported | Nestling | 2002: 2, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
PCB | 1989: 2.19, 1990: 0.792, 1991: 1.55 | Egg concentration | Not Reported | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA |
CHROMIUM (elemental) | BI-89: 0.849, WM-89: 0.813 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDT (2,4'-) | 0.47 ppm ww | Egg concentration | Embryo | 6 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
OXYCHLORDANE | 0.02 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 1997: 0.28, 1998: 0.43 µg/g ww | Stomach concentration | Both Adults and Juveniles | 5 | Carson Lake | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 2.92, reference: 3.30 g | Brain weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 2.34, 2003: 2.36, 2004: 2.32 g | Brain weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
PCB | 0.185 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | S. Wilbur Flood Area | Toxicity Factor Datasets | USA |
COPPER (elemental) | BI-89: 7.16, WM-89: 7.10, WM-91: 7.12, SW-91: 6.21 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DIELDRIN | 0.11 ppm ww | Egg concentration | Embryo | 2 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
CIS-CHLORDANE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 43.65, reference site: 7.92 µg/g ww | Liver concentration | Adult | LCRS: 6, reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA |